Test
Scenario
Interpretation
Used when dealing with large sample sizes or when the population standard deviation is known.
A small p-value (smaller than 0.05) indicates strong evidence against the null hypothesis, leading to its rejection.
Appropriate for small sample sizes or when the population standard deviation is unknown.
Similar to the Z-test
Used for tests of independence or goodness-of-fit.
A small p-value indicates that there is a significant association between the categorical variables, leading to the rejection of the null hypothesis.
Commonly used in Analysis of Variance (ANOVA) to compare variances between groups.
A small p-value suggests that at least one group mean is different from the others, leading to the rejection of the null hypothesis.
Measures the strength and direction of a linear relationship between two continuous variables.
A small p-value indicates that there is a significant linear relationship between the variables, leading to rejection of the null hypothesis that there is no correlation.
In general, a small p-value indicates that the observed data is unlikely to have occurred by random chance alone, which leads to the rejection of the null hypothesis. However, it’s crucial to choose the appropriate test based on the nature of the data and the research question, as well as to interpret the p-value in the context of the specific test being used.
The table given below shows the importance of p-value and shows the various kinds of errors that occur during hypothesis testing.
|
|
|
| Correct decision based | Type I error |
| Type II error | Incorrect decision based |
Type I error: Incorrect rejection of the null hypothesis. It is denoted by α (significance level). Type II error: Incorrect acceptance of the null hypothesis. It is denoted by β (power level)
A researcher wants to investigate whether there is a significant difference in mean height between males and females in a population of university students.
Suppose we have the following data:
Starting with interpreting the process of calculating p-value
H0: There is no significant difference in mean height between males and females.
H1: There is a significant difference in mean height between males and females.
The appropriate test statistic for this scenario is the two-sample t-test, which compares the means of two independent groups.
The t-statistic is a measure of the difference between the means of two groups relative to the variability within each group. It is calculated as the difference between the sample means divided by the standard error of the difference. It is also known as the t-value or t-score.
So, the calculated two-sample t-test statistic (t) is approximately 5.13.
The t-distribution is used for the two-sample t-test . The degrees of freedom for the t-distribution are determined by the sample sizes of the two groups.
The t-distribution is a probability distribution with tails that are thicker than those of the normal distribution.
The degrees of freedom (63) represent the variability available in the data to estimate the population parameters. In the context of the two-sample t-test, higher degrees of freedom provide a more precise estimate of the population variance, influencing the shape and characteristics of the t-distribution.
T-Statistic
The t-distribution is symmetric and bell-shaped, similar to the normal distribution. As the degrees of freedom increase, the t-distribution approaches the shape of the standard normal distribution. Practically, it affects the critical values used to determine statistical significance and confidence intervals.
Step 5 : Calculate Critical Value.
To find the critical t-value with a t-statistic of 5.13 and 63 degrees of freedom, we can either consult a t-table or use statistical software.
We can use scipy.stats module in Python to find the critical t-value using below code.
Comparing with T-Statistic:
The larger t-statistic suggests that the observed difference between the sample means is unlikely to have occurred by random chance alone. Therefore, we reject the null hypothesis.
In case the significance level is not specified, consider the below general inferences while interpreting your results.
Graphically, the p-value is located at the tails of any confidence interval. [As shown in fig 1]
Fig 1: Graphical Representation
The p-value in hypothesis testing is influenced by several factors:
Understanding these factors is crucial for interpreting p-values accurately and making informed decisions in hypothesis testing.
The p-value is a crucial concept in statistical hypothesis testing, serving as a guide for making decisions about the significance of the observed relationship or effect between variables.
Let’s consider a scenario where a tutor believes that the average exam score of their students is equal to the national average (85). The tutor collects a sample of exam scores from their students and performs a one-sample t-test to compare it to the population mean (85).
Since, 0.7059>0.05 , we would conclude to fail to reject the null hypothesis. This means that, based on the sample data, there isn’t enough evidence to claim a significant difference in the exam scores of the tutor’s students compared to the national average. The tutor would accept the null hypothesis, suggesting that the average exam score of their students is statistically consistent with the national average.
The p-value is a crucial concept in statistical hypothesis testing, providing a quantitative measure of the strength of evidence against the null hypothesis. It guides decision-making by comparing the p-value to a chosen significance level, typically 0.05. A small p-value indicates strong evidence against the null hypothesis, suggesting a statistically significant relationship or effect. However, the p-value is influenced by various factors and should be interpreted alongside other considerations, such as effect size and context.
Why is p-value greater than 1.
A p-value is a probability, and probabilities must be between 0 and 1. Therefore, a p-value greater than 1 is not possible.
It means that the observed test statistic is unlikely to occur by chance if the null hypothesis is true. It represents a 1% chance of observing the test statistic or a more extreme one under the null hypothesis.
A good p-value is typically less than or equal to 0.05, indicating that the null hypothesis is likely false and the observed relationship or effect is statistically significant.
It is a measure of the statistical significance of a parameter in the model. It represents the probability of obtaining the observed value of the parameter or a more extreme one, assuming the null hypothesis is true.
A low p-value means that the observed test statistic is unlikely to occur by chance if the null hypothesis is true. It suggests that the observed relationship or effect is statistically significant and not due to random sampling variation.
Compare p-values: Lower p-value indicates stronger evidence against null hypothesis, favoring results with smaller p-values in hypothesis testing.
Similar reads.
Statistical significance is the probability of finding a given deviation from the null hypothesis -or a more extreme one- in a sample. Statistical significance is often referred to as the p-value (short for “probability value”) or simply p in research papers. A small p-value basically means that your data are unlikely under some null hypothesis. A somewhat arbitrary convention is to reject the null hypothesis if p < 0.05 .
I've a coin and my null hypothesis is that it's balanced - which means it has a 0.5 chance of landing heads up. I flip my coin 10 times, which may result in 0 through 10 heads landing up. The probabilities for these outcomes -assuming my coin is really balanced- are shown below. Technically, this is a binomial distribution . The formula for computing these probabilities is based on mathematics and the (very general) assumption of independent and identically distributed variables . Keep in mind that probabilities are relative frequencies. So the 0.24 probability of finding 5 heads means that if I'd draw a 1,000 samples of 10 coin flips, some 24% of those samples should result in 5 heads up.
Now, 9 of my 10 coin flips actually land heads up. The previous figure says that the probability of finding 9 or more heads in a sample of 10 coin flips, p = 0.01 . If my coin is really balanced, the probability is only 1 in 100 of finding what I just found. So, based on my sample of N = 10 coin flips, I reject the null hypothesis : I no longer believe that my coin was balanced after all. Now don't overlook the basic reasoning here: what I want to know is the chance of my coin landing heads up. This parameter is a single numberI estimate this chance by computing the proportion This chance a property of my coin: a fixed number that doesn't fluctuate in any way. What does flucI can estimate this chance by I estimated this chance This is a parameter -a single number that says something about my population of coin flips. I assumed that I drew a sample of 10 coin flips --> Statistical significance reall -->
A sample of 360 people took a grammar test. We'd like to know if male respondents score differently than female respondents. Our null hypothesis is that on average, male respondents score the same number of points as female respondents. The table below summarizes the means and standard deviations for this sample.
Note that females scored 3.5 points higher than males in this sample. However, samples typically differ somewhat from populations. The question is: if the mean scores for all males and all females are equal, then what's the probability of finding this mean difference or a more extreme one in a sample of N = 360? This question is answered by running an independent samples t-test .
So what sample mean differences can we reasonably expect ? Well, this depends on
We therefore standardize our mean difference of 3.5 points, resulting in t = -2.2 So this t-value -our test statistic- is simply the sample mean difference corrected for sample sizes and standard deviations. Interestingly, we know the sampling distribution -and hence the probability- for t.
1-tailed statistical significance is the probability of finding a given deviation from the null hypothesis -or a larger one- in a sample. In our example, p (1-tailed) ≈ 0.014 . The probability of finding t ≤ -2.2 -corresponding to our mean difference of 3.5 points- is 1.4%. If the population means are really equal and we'd draw 1,000 samples, we'd expect only 14 samples to come up with a mean difference of 3.5 points or larger. In short, this sample outcome is very unlikely if the population mean difference is zero. We therefore reject the null hypothesis. Conclusion: men and women probably don't score equally on our test. Some scientists will report precisely these results. However, a flaw here is that our reasoning suggests that we'd retain our null hypothesis if t is large rather than small. A large t-value ends up in the right tail of our distribution . However, our p-value only takes into account the left tail in which our (small) t-value of -2.2 ended up. If we take into account both possibilities, we should report p = 0.028, the 2-tailed significance.
2-tailed statistical significance is the probability of finding a given absolute deviation from the null hypothesis -or a larger one- in a sample. For a t test, very small as well as very large t-values are unlikely under H 0 . Therefore, we shouldn't ignore the right tail of the distribution like we do when reporting a 1-tailed p-value. It suggests that we wouldn't reject the null hypothesis if t had been 2.2 instead of -2.2. However, both t-values are equally unlikely under H 0 . A convention is to compute p for t = -2.2 and the opposite effect : t = 2.2. Adding them results in our 2-tailed p-value: p (2-tailed) = 0.028 in our example. Because the distribution is symmetrical around 0, these 2 p-values are equal. So we may just as well double our 1-tailed p-value.
So should you report the 1-tailed or 2-tailed significance? First off, many statistical tests -such as ANOVA and chi-square tests - only result in a 1-tailed p-value so that's what you'll report. However, the question does apply to t-tests , z-tests and some others. There's no full consensus among data analysts which approach is better. I personally always report 2-tailed p-values whenever available. A major reason is that when some test only yields a 1-tailed p-value, this often includes effects in different directions. “What on earth is he tryi...?” That needs some explanation, right?
We compared young to middle aged people on a grammar test using a t-test . Let's say young people did better. This resulted in a 1-tailed significance of 0.096. This p-value does not include the opposite effect of the same magnitude: middle aged people doing better by the same number of points. The figure below illustrates these scenarios.
We then compared young, middle aged and old people using ANOVA . Young people performed best, old people performed worst and middle aged people are exactly in between. This resulted in a 1-tailed significance of 0.035. Now this p-value does include the opposite effect of the same magnitude.
Now, if p for ANOVA always includes effects in different directions, then why would you not include these when reporting a t-test? In fact, the independent samples t-test is technically a special case of ANOVA: if you run ANOVA on 2 groups, the resulting p-value will be identical to the 2-tailed significance from a t-test on the same data. The same principle applies to the z-test versus the chi-square test.
Reporting 1-tailed significance is sometimes defended by claiming that the researcher is expecting an effect in a given direction. However, I cannot verify that. Perhaps such “alternative hypotheses” were only made up in order to render results more statistically significant. Second, expectations don't rule out possibilities . If somebody is absolutely sure that some effect will have some direction, then why use a statistical test in the first place?
So what does “statistical significance” really tell us? Well, it basically says that some effect is very probably not zero in some population. So is that what we really want to know? That a mean difference, correlation or other effect is “not zero”? No. Of course not. We really want to know how large some mean difference, correlation or other effect is. However, that's not what statistical significance tells us. For example, a correlation of 0.1 in a sample of N = 1,000 has p ≈ 0.0015. This is highly statistically significant : the population correlation is very probably not 0.000... However, a 0.1 correlation is not distinguishable from 0 in a scatterplot . So it's probably not practically significant . Reversely, a 0.5 correlation with N = 10 has p ≈ 0.14 and hence is not statistically significant. Nevertheless, a scatterplot shows a strong relation between our variables. However, since our sample size is very small, this strong relation may very well be limited to our small sample: it has a 14% chance of occurring if our population correlation is really zero.
The basic problem here is that any effect is statistically significant if the sample size is large enough. And therefore, results must have both statistical and practical significance in order to carry any importance. effect size . --> Confidence intervals nicely combine these two pieces of information and can thus be argued to be more useful than just statistical significance.
Thanks for reading!
The basic problem here is that any effect is statistically significant if the sample size is large enough. And therefore, we should take into account both statistical and practical significance when evaluating results. We should therefore only
This tutorial has 14 comments:.
God may bless you
A p-value, or a confidence interval maybe referred to for claiming the so-called "statistical significance". However, both are continuous variables. Any attempt to dichotomize or categorize a continuous variable will be logically not defensible. Therefore, forget about "Statistically significance" entirely!
It is very obvious that Test of significance is a bedrock of research works.
Thank you for visiting nature.com. You are using a browser version with limited support for CSS. To obtain the best experience, we recommend you use a more up to date browser (or turn off compatibility mode in Internet Explorer). In the meantime, to ensure continued support, we are displaying the site without styles and JavaScript.
Nature Plants ( 2024 ) Cite this article
Metrics details
Elton’s biotic resistance hypothesis posits that species-rich communities are more resistant to invasion. However, it remains unknown how species, phylogenetic and functional richness, along with environmental and human-impact factors, collectively affect plant invasion as alien species progress along the introduction–naturalization–invasion continuum. Using data from 12,056 local plant communities of the Czech Republic, this study reveals varying effects of these factors on the presence and richness of alien species at different invasion stages, highlighting the complexity of the invasion process. Specifically, we demonstrate that although species richness and functional richness of resident communities had mostly negative effects on alien species presence and richness, the strength and sometimes also direction of these effects varied along the continuum. Our study not only underscores that evidence for or against Elton’s biotic resistance hypothesis may be stage-dependent but also suggests that other invasion hypotheses should be carefully revisited given their potential stage-dependent nature.
This is a preview of subscription content, access via your institution
Access Nature and 54 other Nature Portfolio journals
Get Nature+, our best-value online-access subscription
24,99 € / 30 days
cancel any time
Subscribe to this journal
Receive 12 digital issues and online access to articles
111,21 € per year
only 9,27 € per issue
Buy this article
Prices may be subject to local taxes which are calculated during checkout
The data used in this study were obtained from these sources: the data on vegetation plots were from the Czech National Phytosociological Database 54 ( https://botzool.cz/vegsci/phytosociologicalDb/ ); species’ statuses along the invasion continuum were extracted from Pyšek et al. 55 ; the three leaf traits required for CSR calculation were collected from the Pladias Database of the Czech Flora and Vegetation 58 and other publications 61 , 62 , 63 , 64 , 65 , 66 ; species CSR scores were calculated using the StrateFy tool 60 ; climatic variables were extracted from Tolasz 73 ; soil pH was collected from the Land Use/Land Cover Area Frame Survey 74 ; and the human population density of the cadastral area where each plot located was obtained from the Digital Vector Database of Czech Republic ArcČR v.4.0 (ref. 75 ). The data that support the findings of this study are available via GitHub at https://github.com/kun-ecology/BioticResistance_InvasionContinuum and via Zenodo at https://doi.org/10.5281/zenodo.12818669 (ref. 79 ).
R functions for the computation of phylogenetic and functional metrics have been deposited on GitHub ( https://github.com/kun-ecology/ecoloop ). R scripts for reproducing the analyses and figures are available via GitHub at https://github.com/kun-ecology/BioticResistance_InvasionContinuum and via Zenodo at https://doi.org/10.5281/zenodo.12818669 (ref. 79 ).
Roy, H. E. et al. (eds) Summary for Policymakers of the Thematic Assessment Report on Invasive Alien Species and Their Control of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES Secretariat, 2023).
Spatz, D. R. et al. Globally threatened vertebrates on islands with invasive species. Sci. Adv. 3 , e1603080 (2017).
Article PubMed PubMed Central Google Scholar
Walsh, J. R., Carpenter, S. R. & Vander Zanden, M. J. Invasive species triggers a massive loss of ecosystem services through a trophic cascade. Proc. Natl Acad. Sci. USA 113 , 4081–4085 (2016).
Article CAS PubMed PubMed Central Google Scholar
Liu, C. et al. Economic costs of biological invasions in Asia. NeoBiota 67 , 53–78 (2021).
Article Google Scholar
Capinha, C., Essl, F., Porto, M. & Seebens, H. The worldwide networks of spread of recorded alien species. Proc. Natl Acad. Sci. USA 120 , e2201911120 (2023).
Article CAS PubMed Google Scholar
Seebens, H. et al. Projecting the continental accumulation of alien species through to 2050. Glob. Change Biol. 27 , 970–982 (2021).
Article CAS Google Scholar
Richardson, D. M. & Pyšek, P. Plant invasions: merging the concepts of species invasiveness and community invasibility. Prog. Phys. Geogr. 30 , 409–431 (2006).
Elton, C. S. The Ecology of Invasions by Animals and Plants (Univ. Chicago Press, 1958).
Bach, W. et al. Phylogenetic composition of native island floras influences naturalized alien species richness. Ecography 2022 , e06227 (2022).
Beaury, E. M., Finn, J. T., Corbin, J. D., Barr, V. & Bradley, B. A. Biotic resistance to invasion is ubiquitous across ecosystems of the United States. Ecol. Lett. 23 , 476–482 (2020).
Article PubMed Google Scholar
Lefebvre, S., Segar, J. & Staude, I. R. Non-natives are linked to higher plant diversity across spatial scales. J. Biogeogr. 51 , 1290–1298 (2024).
Fridley, J. D. et al. The invasion paradox: reconciling pattern and process in species invasion. Ecology 88 , 3–17 (2007).
Herben, T., Mandák, B., Bímová, K. & Münzbergová, Z. Invasibility and species richness of a community: a neutral model and a survey of published data. Ecology 85 , 3223–3233 (2004).
Jeschke, J. M. et al. Taxonomic bias and lack of cross-taxonomic studies in invasion biology. Front. Ecol. Environ. 10 , 349–350 (2012).
Jeschke, J. M. General hypotheses in invasion ecology. Divers. Distrib. 20 , 1229–1234 (2014).
Stohlgren, T. J., Barnett, D. T. & Kartesz, J. T. The rich get richer: patterns of plant invasions in the United States. Front. Ecol. Environ. 1 , 11–14 (2003).
Shea, K. & Chesson, P. Community ecology theory as a framework for biological invasions. Trends Ecol. Evol. 17 , 170–176 (2002).
Delavaux, C. S. et al. Native diversity buffers against severity of non-native tree invasions. Nature 621 , 773–781 (2023).
Blackburn, T. M. et al. A proposed unified framework for biological invasions. Trends Ecol. Evol. 26 , 333–339 (2011).
Pyšek, P. & Richardson, D. M. Invasive species, environmental change and management, and health. Annu. Rev. Environ. Resour. 35 , 25–55 (2010).
Daly, E. Z. et al. A synthesis of biological invasion hypotheses associated with the introduction–naturalisation–invasion continuum. Oikos 2023 , e09645 (2023).
Guo, K. et al. Ruderals naturalize, competitors invade: varying roles of plant adaptive strategies along the invasion continuum. Funct. Ecol. 36 , 2469–2479 (2022).
Pyšek, P. et al. Small genome size and variation in ploidy levels support the naturalization of vascular plants but constrain their invasive spread. N. Phytol. 239 , 2389–2403 (2023).
Omer, A. et al. The role of phylogenetic relatedness on alien plant success depends on the stage of invasion. Nat. Plants 8 , 906–914 (2022).
Guo, K. et al. Plant invasion and naturalization are influenced by genome size, ecology and economic use globally. Nat. Commun. 15 , 1330 (2024).
Richardson, D. M. & Pyšek, P. Naturalization of introduced plants: ecological drivers of biogeographical patterns. N. Phytol. 196 , 383–396 (2012).
Byun, C., De Blois, S. & Brisson, J. Plant functional group identity and diversity determine biotic resistance to invasion by an exotic grass. J. Ecol. 101 , 128–139 (2013).
Banerjee, A. K. et al. Not just with the natives, but phylogenetic relationship between stages of the invasion process determines invasion success of alien plant species. Preprint at https://doi.org/10.1101/2022.10.12.512006 (2022).
Cubino, J. P., Těšitel, J., Fibich, P., Lepš, J. & Chytrý, M. Alien plants tend to occur in species-poor communities. NeoBiota 73 , 39–56 (2022).
Lannes, L. S. et al. Species richness both impedes and promotes alien plant invasions in the Brazilian Cerrado. Sci. Rep. 10 , 11365 (2020).
Stohlgren, T. J. et al. Exotic plant species invade hot spots of native plant diversity. Ecol. Monogr. 69 , 25–46 (1999).
Davidson, A. M., Jennions, M. & Nicotra, A. B. Do invasive species show higher phenotypic plasticity than native species and, if so, is it adaptive? A meta-analysis. Ecol. Lett. 14 , 419–431 (2011).
Lau, J. A. & Funk, J. L. How ecological and evolutionary theory expanded the ‘ideal weed’ concept. Oecologia 203 , 251–266 (2023).
Prentis, P. J., Wilson, J. R. U., Dormontt, E. E., Richardson, D. M. & Lowe, A. J. Adaptive evolution in invasive species. Trends Plant Sci. 13 , 288–294 (2008).
Stohlgren, T., Jarnevich, C. S., Chong, G. W. & Evangelista, P. Scale and plant invasions: a theory of biotic acceptance. Preslia 78 , 405–426 (2006).
Google Scholar
Cavieres, L. A. Facilitation and the invasibility of plant communities. J. Ecol. 109 , 2019–2028 (2021).
Catford, J. A., Vesk, P. A., Richardson, D. M. & Pyšek, P. Quantifying levels of biological invasion: towards the objective classification of invaded and invasible ecosystems. Glob. Change Biol. 18 , 44–62 (2012).
Su, G., Mertel, A., Brosse, S. & Calabrese, J. M. Species invasiveness and community invasibility of North American freshwater fish fauna revealed via trait-based analysis. Nat. Commun. 14 , 2332 (2023).
Parker, J. D. et al. Do invasive species perform better in their new ranges? Ecology 94 , 985–994 (2013).
Iseli, E. et al. Rapid upwards spread of non-native plants in mountains across continents. Nat. Ecol. Evol. 7 , 405–413 (2023).
Pauchard, A. et al. Ain’t no mountain high enough: plant invasions reaching new elevations. Front. Ecol. Environ. 7 , 479–486 (2009).
Zheng, M.-M., Pyšek, P., Guo, K., Hasigerili, H. & Guo, W.-Y. Clonal alien plants in the mountains spread upward more extensively and faster than non-clonal. Neobiota 91 , 29–48 (2024).
Zu, K. et al. Elevational shift in seed plant distributions in China’s mountains over the last 70 years. Glob. Ecol. Biogeogr. 32 , 1098–1112 (2023).
Reeve, S. et al. Rare, common, alien and native species follow different rules in an understory plant community. Ecol. Evol. 12 , e8734 (2022).
Hartemink, A. E. & Barrow, N. J. Soil pH–nutrient relationships: the diagram. Plant Soil 486 , 209–215 (2023).
Dawson, W., Rohr, R. P., van Kleunen, M. & Fischer, M. Alien plant species with a wider global distribution are better able to capitalize on increased resource availability. N. Phytol. 194 , 859–867 (2012).
Dawson, W. et al. Global hotspots and correlates of alien species richness across taxonomic groups. Nat. Ecol. Evol. 1 , 0186 (2017).
Pyšek, P. et al. Disentangling the role of environmental and human pressures on biological invasions across Europe. Proc. Natl Acad. Sci. USA 107 , 12157–12162 (2010).
Damgaard, C. A critique of the space-for-time substitution practice in community ecology. Trends Ecol. Evol. 34 , 416–421 (2019).
Hejda, M., Pyšek, P. & Jarošík, V. Impact of invasive plants on the species richness, diversity and composition of invaded communities. J. Ecol. 97 , 393–403 (2009).
Lovell, R. S. L., Collins, S., Martin, S. H., Pigot, A. L. & Phillimore, A. B. Space-for-time substitutions in climate change ecology and evolution. Biol. Rev. 98 , 2243–2270 (2023).
Thomaz, S. M. et al. Using space-for-time substitution and time sequence approaches in invasion ecology. Freshw. Biol. 57 , 2401–2410 (2012).
Wogan, G. O. U. & Wang, I. J. The value of space‐for‐time substitution for studying fine‐scale microevolutionary processes. Ecography 41 , 1456–1468 (2018).
Chytrý, M. & Rafajová, M. Czech National Phytosociological Database: basic statistics of the available vegetation-plot data. Preslia 75 , 1–15 (2003).
Pyšek, P. et al. Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. Preslia 94 , 447–577 (2022).
Divíšek, J. et al. Similarity of introduced plant species to native ones facilitates naturalization, but differences enhance invasion success. Nat. Commun. 9 , 4631 (2018).
Raunkiaer, C. The Life Forms of Plants and Statistical Plant Geography (Clarendon, 1934).
Chytrý, M. et al. Pladias Database of the Czech flora and vegetation. Preslia 93 , 1–87 (2021).
Li, D. rtrees: an R package to assemble phylogenetic trees from megatrees. Ecography 2023 , e06643 (2023).
Pierce, S. et al. A global method for calculating plant CSR ecological strategies applied across biomes world-wide. Funct. Ecol. 31 , 444–457 (2017).
Díaz, S. et al. The global spectrum of plant form and function: enhanced species-level trait dataset. Sci. Data 9 , 755 (2022).
Guo, W.-Y. et al. The role of adaptive strategies in plant naturalization. Ecol. Lett. 21 , 1380–1389 (2018).
Guo, W.-Y. et al. Domestic gardens play a dominant role in selecting alien species with adaptive strategies that facilitate naturalization. Glob. Ecol. Biogeogr. 28 , 628–639 (2019).
Tavşanoǧlu, Ç. & Pausas, J. G. A functional trait database for Mediterranean Basin plants. Sci. Data 51 , 180135 (2018).
Bjorkman, A. D. et al. Tundra Trait Team: a database of plant traits spanning the tundra biome. Glob. Ecol. Biogeogr. 27 , 1402–1411 (2018).
Kattge, J. et al. TRY plant trait database—enhanced coverage and open access. Glob. Change Biol. 26 , 119–188 (2020).
Goolsby, E. W., Bruggeman, J. & Ané, C. Rphylopars: fast multivariate phylogenetic comparative methods for missing data and within-species variation. Methods Ecol. Evol. 8 , 22–27 (2017).
Matthews, T. J. et al. A global analysis of avian island diversity–area relationships in the Anthropocene. Ecol. Lett. 26 , 965–982 (2023).
Cardoso, P. et al. Calculating functional diversity metrics using neighbor-joining trees. Ecography https://doi.org/10.1101/2022.11.27.518065 (2022).
Cardoso, P., Rigal, F. & Carvalho, J. C. BAT—Biodiversity Assessment Tools, an R package for the measurement and estimation of alpha and beta taxon, phylogenetic and functional diversity. Methods Ecol. Evol. 6 , 232–236 (2015).
Swenson, N. G. Functional and Phylogenetic Ecology in R (Springer, 2014).
Loiola, P. P. et al. Invaders among locals: alien species decrease phylogenetic and functional diversity while increasing dissimilarity among native community members. J. Ecol. 106 , 2230–2241 (2018).
Tolasz, R. et al. Atlas Podnebí Česka—Climate Atlas of Czechia (Czech Hydrometeorological Institute and Palacký Univ., 2007).
Ballabio, C. et al. Mapping LUCAS topsoil chemical properties at European scale using Gaussian process regression. Geoderma 355 , 113912 (2019).
Digital Vector Database of Czech Republic ArcČR v.4.0 (ČÚZK, ČSÚ and ArcDATA Prague, 2021).
Lindgren, F. & Rue, H. Bayesian spatial modelling with R-INLA. J. Stat. Softw. 63 , 1–25 (2015).
Schielzeth, H. Simple means to improve the interpretability of regression coefficients. Methods Ecol. Evol. 1 , 103–113 (2010).
R Core Team. R: A Language and Environment for Statistical Computing http://www.R-project.org/ (R Foundation for Statistical Computing, 2023).
Guo, K. et al. Stage dependence of Elton’s biotic resistance hypothesis of biological invasions. Zenodo https://doi.org/10.5281/zenodo.12818669 (2024).
Download references
K.G. and W.-Y.G. were supported by the Natural Science Foundation of China (grant no. 32171588, awarded to W.-Y.G.) and the Shanghai Pujiang Program (grant no. 21PJ1402700, awarded to W.-Y.G.). K.G. was also supported by the Shanghai Sailing Program (grant no. 22YF1411700) and the Natural Science Foundation of China (grant no. 32301386). P.P. was supported by the Czech Science Foundation (EXPRO grant no. 19-28807X) and the Czech Academy of Sciences (long-term research development project RVO 67985939). M.C. and Z.L. were supported by the Czech Science Foundation (EXPRO grant no. 19-28491X). J.D. was supported by the Technology Agency of the Czech Republic (grant no. SS02030018). M.S. was funded by the project GEOSANT with the funding organization Masaryk University (MUNI/A/1469/2023).
Authors and affiliations.
Zhejiang Tiantong Forest Ecosystem National Observation and Research Station, Shanghai Key Lab for Urban Ecological Processes and Eco-Restoration & Research Center for Global Change and Complex Ecosystems, School of Ecological and Environmental Sciences, East China Normal University, Shanghai, People’s Republic of China
Kun Guo & Wen-Yong Guo
Department of Invasion Ecology, Institute of Botany, Czech Academy of Sciences, Průhonice, Czech Republic
Department of Ecology, Faculty of Science, Charles University, Prague, Czech Republic
Department of Botany and Zoology, Faculty of Science, Masaryk University, Brno, Czech Republic
Milan Chytrý, Jan Divíšek, Martina Sychrová & Zdeňka Lososová
Department of Geography, Faculty of Science, Masaryk University, Brno, Czech Republic
Jan Divíšek & Martina Sychrová
Ecology, Department of Biology, University of Konstanz, Konstanz, Germany
Mark van Kleunen
Zhejiang Provincial Key Laboratory of Plant Evolutionary Ecology and Conservation, Taizhou University, Taizhou, People’s Republic of China
Department of Agricultural and Environmental Sciences (DiSAA), University of Milan, Milan, Italy
Simon Pierce
Zhejiang Zhoushan Island Ecosystem Observation and Research Station, Zhoushan, People’s Republic of China
Wen-Yong Guo
State Key Laboratory of Estuarine and Coastal Research, East China Normal University, Shanghai, People’s Republic of China
You can also search for this author in PubMed Google Scholar
K.G., P.P. and W.-Y.G. conceptualized the research. P.P., M.C., J.D., M.S. and W.-Y.G. provided the data. K.G. analysed the data and drafted the paper, with substantial contributions from all authors.
Correspondence to Wen-Yong Guo .
Competing interests.
The authors declare no competing interests.
Peer review information.
Nature Plants thanks Martha Hoopes and Johannes Kollmann for their contribution to the peer review of this work.
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary information.
Supplementary Figs. 1–8.
Rights and permissions.
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
Reprints and permissions
Cite this article.
Guo, K., Pyšek, P., Chytrý, M. et al. Stage dependence of Elton’s biotic resistance hypothesis of biological invasions. Nat. Plants (2024). https://doi.org/10.1038/s41477-024-01790-0
Download citation
Received : 18 April 2024
Accepted : 15 August 2024
Published : 03 September 2024
DOI : https://doi.org/10.1038/s41477-024-01790-0
Anyone you share the following link with will be able to read this content:
Sorry, a shareable link is not currently available for this article.
Provided by the Springer Nature SharedIt content-sharing initiative
Sign up for the Nature Briefing newsletter — what matters in science, free to your inbox daily.
You are accessing a machine-readable page. In order to be human-readable, please install an RSS reader.
All articles published by MDPI are made immediately available worldwide under an open access license. No special permission is required to reuse all or part of the article published by MDPI, including figures and tables. For articles published under an open access Creative Common CC BY license, any part of the article may be reused without permission provided that the original article is clearly cited. For more information, please refer to https://www.mdpi.com/openaccess .
Feature papers represent the most advanced research with significant potential for high impact in the field. A Feature Paper should be a substantial original Article that involves several techniques or approaches, provides an outlook for future research directions and describes possible research applications.
Feature papers are submitted upon individual invitation or recommendation by the scientific editors and must receive positive feedback from the reviewers.
Editor’s Choice articles are based on recommendations by the scientific editors of MDPI journals from around the world. Editors select a small number of articles recently published in the journal that they believe will be particularly interesting to readers, or important in the respective research area. The aim is to provide a snapshot of some of the most exciting work published in the various research areas of the journal.
Original Submission Date Received: .
Find support for a specific problem in the support section of our website.
Please let us know what you think of our products and services.
Visit our dedicated information section to learn more about MDPI.
Barriers to digital services trade and export efficiency of digital services.
2. literature review, 3. research design, 3.1. model construction, 3.2. data description, 4. empirical analysis, 4.1. stochastic frontier gravity model, 4.2. trade inefficiency model, 4.3. robustness test, 5. extended analysis, 6. discussion and conclusions, 6.1. discussion, 6.2. conclusions, 6.3. recommendations, author contributions, institutional review board statement, informed consent statement, data availability statement, conflicts of interest.
Click here to enlarge figure
Variable | Time-Invariant Model | Time-Variant Model | ||
---|---|---|---|---|
Coefficient | t-Value | Coefficient | t-Value | |
0.760 *** | 34.90 | 0.658 *** | 28.62 | |
0.291 *** | 8.31 | 0.193 *** | 5.48 | |
0.848 *** | 39.63 | 0.771 *** | 34.49 | |
0.174 *** | 5.09 | 0.0921 ** | 2.63 | |
−1.179 *** | −34.62 | −1.150 *** | −33.08 | |
1.140 *** | 8.09 | 1.231 *** | 8.36 | |
Constant | −7.836 *** | −12.15 | −1.367 | −0.98 |
μ | 4.267 *** | 13.39 | 6.626 *** | 5.28 |
γ | 0.885 *** | 197.10 | 0.897 *** | 215.57 |
η | 0.006 *** | 5.48 | ||
N | 12,532 | 12,532 | ||
LR1 | 538.289 | p-value | 0.000 | |
LR2 | 770.481 | p-value | 0.000 | |
LR3 | 68.996 | p-value | 0.000 |
Stochastic Frontier Gravity Model | Trade Inefficiency Model | ||||
---|---|---|---|---|---|
Variable | Coefficient | t-Value | Variable | Coefficient | t-Value |
0.780 *** | 100.24 | −0.186 | −1.09 | ||
0.801 *** | 44.60 | 0.980 *** | 3.28 | ||
0.860 *** | 117.83 | −1.765 *** | −5.15 | ||
0.560 *** | 38.28 | 2.904 *** | 6.72 | ||
−1.072 *** | −92.51 | −4.117 *** | −5.42 | ||
0.745 *** | 15.89 | Constant | 0.805 * | 2.13 | |
Constant | −21.69 *** | −74.67 | N | 12,532 | |
LR | 354.150 | p-value | 0.000 |
Variable | (1) | (2) | (3) | (4) | ||||
---|---|---|---|---|---|---|---|---|
Coefficient | t-Value | Coefficient | t-Value | Coefficient | t-Value | Coefficient | t-Value | |
−0.175 | −1.15 | −0.066 | −0.30 | −0.074 | −0.59 | −0.153 | −1.10 | |
0.806 *** | 2.87 | 1.213 ** | 2.51 | 0.649 *** | 3.86 | 0.612 *** | 2.74 | |
−1.396 *** | −4.99 | −1.477 *** | −4.08 | −2.787 *** | −7.40 | −1.468 *** | −5.44 | |
2.506 *** | 6.44 | 2.852 *** | 4.97 | 1.472 *** | 11.52 | 2.390 *** | 7.38 | |
−3.282 *** | −4.93 | −3.567 *** | −3.81 | −3.992 *** | −11.29 | −3.244 *** | −5.57 | |
Constant | 1.144 *** | 3.63 | 1.282 *** | 3.73 | 1.829 *** | 10.12 | 1.153 *** | 4.00 |
N | 9,193 | 3,982 | 5,211 | 11,473 |
The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
Wang, X.; Zhang, J.; Zhu, Y. Barriers to Digital Services Trade and Export Efficiency of Digital Services. Sustainability 2024 , 16 , 7517. https://doi.org/10.3390/su16177517
Wang X, Zhang J, Zhu Y. Barriers to Digital Services Trade and Export Efficiency of Digital Services. Sustainability . 2024; 16(17):7517. https://doi.org/10.3390/su16177517
Wang, Xiaomei, Jia Zhang, and Yixin Zhu. 2024. "Barriers to Digital Services Trade and Export Efficiency of Digital Services" Sustainability 16, no. 17: 7517. https://doi.org/10.3390/su16177517
Article access statistics, further information, mdpi initiatives, follow mdpi.
Subscribe to receive issue release notifications and newsletters from MDPI journals
IMAGES
VIDEO
COMMENTS
The p value is a proportion: if your p value is 0.05, that means that 5% of the time you would see a test statistic at least as extreme as the one you found if the null hypothesis was true. Example: Test statistic and p value If the mice live equally long on either diet, then the test statistic from your t test will closely match the test ...
One of the most commonly used p-value is 0.05. If the calculated p-value turns out to be less than 0.05, the null hypothesis is considered to be false, or nullified (hence the name null hypothesis). And if the value is greater than 0.05, the null hypothesis is considered to be true. Let me elaborate a bit on that.
The null hypothesis states that there is no statistical difference between groups based on the stated research hypothesis. ... For example, a p-value from a double-blinded randomized clinical trial (designed to minimize bias) should be weighted higher than one from a retrospective observational study .
Null Hypothesis Examples. Null hypotheses start as research questions that the investigator rephrases as a statement indicating there is no effect or relationship. Research Question: ... Reject the null hypothesis when the p-value is less than or equal to your significance level. Your sample data favor the alternative hypothesis, which suggests ...
S.3.2 Hypothesis Testing (P-Value Approach) The P -value approach involves determining "likely" or "unlikely" by determining the probability — assuming the null hypothesis was true — of observing a more extreme test statistic in the direction of the alternative hypothesis than the one observed. If the P -value is small, say less than (or ...
Here is the technical definition of P values: P values are the probability of observing a sample statistic that is at least as extreme as your sample statistic when you assume that the null hypothesis is true. Let's go back to our hypothetical medication study. Suppose the hypothesis test generates a P value of 0.03.
A p-value, or probability value, is a number describing how likely it is that your data would have occurred by random chance (i.e., that the null hypothesis is true). The level of statistical significance is often expressed as a p-value between 0 and 1. The smaller the p -value, the less likely the results occurred by random chance, and the ...
Null hypothesis value: 260; Let's work through the step-by-step process of how to calculate a p-value. First, we need to identify the correct test statistic. Because we're comparing one mean to a null value, we need to use a 1-sample t-test. ... Displaying the P value in a Chart. In the example above, you saw how to calculate a p-value ...
The p value is the evidence against a null hypothesis. The smaller the p-value, the stronger the evidence that you should reject the null hypothesis. P values are expressed as decimals although it may be easier to understand what they are if you convert them to a percentage. For example, a p value of 0.0254 is 2.54%.
The p -value is used in the context of null hypothesis testing in order to quantify the statistical significance of a result, the result being the observed value of the chosen statistic . [note 2] The lower the p -value is, the lower the probability of getting that result if the null hypothesis were true. A result is said to be statistically ...
The textbook definition of a p-value is: A p-value is the probability of observing a sample statistic that is at least as extreme as your sample statistic, given that the null hypothesis is true. For example, suppose a factory claims that they produce tires that have a mean weight of 200 pounds. An auditor hypothesizes that the true mean weight ...
The null hypothesis (H0) answers "No, there's no effect in the population.". The alternative hypothesis (Ha) answers "Yes, there is an effect in the population.". The null and alternative are always claims about the population. That's because the goal of hypothesis testing is to make inferences about a population based on a sample.
The observed value is statistically significant (p ≤ 0.05), so the null hypothesis (N0) is rejected, and the alternative hypothesis (Ha) is accepted. Usually, a researcher uses a confidence level of 95% or 99% (p-value of 0.05 or 0.01) as general guidelines to decide if you should reject or keep the null.
If you're seeing this message, it means we're having trouble loading external resources on our website. If you're behind a web filter, please make sure that the domains *.kastatic.org and *.kasandbox.org are unblocked.
A corresponding p value that tells you the probability of obtaining this result if the null hypothesis is true. The p value determines statistical significance. An extremely low p value indicates high statistical significance, while a high p value means low or no statistical significance. Example: Hypothesis testing To test your hypothesis, you ...
P value was to be used as a rough numerical guide of the strength of evidence against the null hypothesis." 4. One common mistake in using the P value is to declare a result as "significant" if the P value is less than .05. We want to avoid this common and costly mistake. In addition, here are twelve additional misconceptions of the P
H 0 (Null Hypothesis): Population parameter =, ≤, ≥ some value. H A (Alternative Hypothesis): Population parameter <, >, ≠ some value. Note that the null hypothesis always contains the equal sign. We interpret the hypotheses as follows: Null hypothesis: The sample data provides no evidence to support some claim being made by an individual.
If the p-value is not less than the significance level, then you fail to reject the null hypothesis. You can use the following clever line to remember this rule: "If the p is low, the null must go." In other words, if the p-value is low enough then we must reject the null hypothesis. The following examples show when to reject (or fail to ...
The p-value or probability value is a number, calculated from a statistical test, that tells how likely it is that your results would have occurred under the null hypothesis of the test. P-values are usually automatically calculated using statistical software. They can also be calculated using p-value tables for the relevant statistical test.
Output: t-statistic: -0.3895364838967159 p-value: 0.7059365203154573 Fail to reject the null hypothesis. The difference is not statistically significant. Since, 0.7059>0.05, we would conclude to fail to reject the null hypothesis.This means that, based on the sample data, there isn't enough evidence to claim a significant difference in the exam scores of the tutor's students compared to ...
Statistical significance is often referred to as the p-value (short for "probability value") or simply p in research papers. A small p-value basically means that your data are unlikely under some null hypothesis. A somewhat arbitrary convention is to reject the null hypothesis if p < 0.05. Example 1 - 10 Coin Flips. I've a coin and my null ...
proportions. Testing of hypothesis; Null and alternate hypothesis, Neyman Pearson fundamental lemma, Tests for one sample and two sample problems for normal populations, testsfor proportions. Course Reference: 1. Introduction to Mathematical Statistics, by R V Hogg, A Craig and J W McKean; 2. An
Specifically, SES was calculated as (X obs - mean(X null))/s.d.(X null), where X obs is the observed value of each metric, while mean(X null) and s.d.(X null) are the average and standard ...
The likelihood ratio statistic LR = −2 [L (H0) − L (H1)] was constructed for testing, where L (H0) and L (H1) are values of the likelihood function under a null hypothesis and alternative hypothesis, respectively. First, we set the null hypothesis that there was no trade inefficiency, namely, μ = 0, to test whether the trade inefficiency ...